US6620396B2 - Method of removing phosphorus from sludge - Google Patents
Method of removing phosphorus from sludge Download PDFInfo
- Publication number
- US6620396B2 US6620396B2 US09/859,254 US85925401A US6620396B2 US 6620396 B2 US6620396 B2 US 6620396B2 US 85925401 A US85925401 A US 85925401A US 6620396 B2 US6620396 B2 US 6620396B2
- Authority
- US
- United States
- Prior art keywords
- phosphorus
- sludge
- water
- phosphate salt
- sodium
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Expired - Fee Related, expires
Links
- APQKIGWLBGHOQR-UHFFFAOYSA-N COP(=O)(OC)OP(=O)(OC)OP(=O)(OC)OC Chemical compound COP(=O)(OC)OP(=O)(OC)OP(=O)(OC)OC APQKIGWLBGHOQR-UHFFFAOYSA-N 0.000 description 3
- VKBOOXDDMMMSCM-UHFFFAOYSA-A O=P(O[Na])(O[Na])OP(=O)(O[Na])OP(=O)(O[Na])O[Na].O=P(O[Na])(O[Na])OP(=O)(O[Na])OP(=O)(O[Na])O[Na].O=P(O[Na])(O[Na])OP(=O)(O[Na])O[Na] Chemical compound O=P(O[Na])(O[Na])OP(=O)(O[Na])OP(=O)(O[Na])O[Na].O=P(O[Na])(O[Na])OP(=O)(O[Na])OP(=O)(O[Na])O[Na].O=P(O[Na])(O[Na])OP(=O)(O[Na])O[Na] VKBOOXDDMMMSCM-UHFFFAOYSA-A 0.000 description 1
Classifications
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F11/00—Treatment of sludge; Devices therefor
-
- C—CHEMISTRY; METALLURGY
- C01—INORGANIC CHEMISTRY
- C01B—NON-METALLIC ELEMENTS; COMPOUNDS THEREOF; METALLOIDS OR COMPOUNDS THEREOF NOT COVERED BY SUBCLASS C01C
- C01B25/00—Phosphorus; Compounds thereof
- C01B25/02—Preparation of phosphorus
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/58—Treatment of water, waste water, or sewage by removing specified dissolved compounds
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/001—Processes for the treatment of water whereby the filtration technique is of importance
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/02—Treatment of water, waste water, or sewage by heating
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/38—Treatment of water, waste water, or sewage by centrifugal separation
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2101/00—Nature of the contaminant
- C02F2101/10—Inorganic compounds
- C02F2101/105—Phosphorus compounds
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y10—TECHNICAL SUBJECTS COVERED BY FORMER USPC
- Y10S—TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y10S210/00—Liquid purification or separation
- Y10S210/902—Materials removed
- Y10S210/906—Phosphorus containing
Definitions
- This invention relates to a method of recovering phosphorus from phosphorus-containing sludge.
- it relates to the treatment of this sludge with a phosphate salt which, on further processing, causes the phosphorus particles to coalesce into a separate phosphorus phase.
- Sludge from manufacturing phosphorus can contain small amounts of phosphorus and dirt particles dispersed in an aqueous phase.
- the phosphorus should be removed from the sludge for both economic and environmental reasons.
- the phosphorus cannot be recovered from the sludge by filtration because most of the filtered phosphorus stays dispersed in water.
- Phosphorus can be recovered from this sludge by heating the sludge in the absence of air to evaporate the water, but that is uneconomic.
- Various substances can be added to the sludge to cause the phosphorus particles to coalesce but, until now, this has not been very effective.
- This invention is applicable to aqueous sludges containing dispersed phosphorus particles as a discontinuous phase.
- the amount of phosphorus in the sludge should be at least about 1 wt % (based on sludge weight) because it is usually not economical to treat sludges containing less phosphorus by the method of this invention.
- Sludges that contain more than about 15 wt % phosphorus and have a continuous phosphorus phase can usually be treated more economically by other methods.
- the sludge contains about 5 to about 10 wt % phosphorus.
- the phosphorus is present as water-dispersed particles of P 4 that are too small to readily settle out.
- Particles of “dirt” and other charged impurities may keep the phosphorus particles in suspension and prevent them from agglomerating.
- the “dirt” is a mixture of a variety of substances, such as coke, sand, phosphate rock, etc.
- aqueous sludge is placed in a tank and a phosphate salt that has the general formula
- R is an alkali metal or ammonium and n is 0 to 30.
- n is 0 to 12 and R is sodium or potassium as many of those salts are commercially available; sodium salts are most preferred as they are less expensive.
- Many of the phosphate salts are commercially available and those that aren't can be made using processes similar to the those used to prepare the commercially available phosphate salts.
- the preferred phosphate salts are sodium tripolyphosphate (STPP), tetrasodium pyrophosphate (TSPP), and sodium hexametaphosphate (SHMP), which have the respective formulas:
- phosphate salts are preferred as they have been found to work well and are commercially available.
- the amount of phosphate salt added to the sludge should be about 1 to about 20 wt %, based on the weight of the phosphorus in the sludge, as less is not very effective and more is usually unnecessary and without additional benefit; preferably, about 2 to about 10 wt % of the phosphate salt is added.
- the sludge Before or after the addition of the phosphate salt, the sludge is heated above the melting point of phosphorus, 44.1° C.; preferably, it is heated to about 50 to about 70° C. It is preferable to stir for about 5 to about 60 minutes while heating.
- the sludge is then filtered, preferably under a pressure of about 10 to about 100 psi, or it can be centrifuged. Water and the liquid phosphorus in the aqueous phase pass through as the filtrate and the dirt forms a filter cake. Filtered or centrifuged phosphorus particles agglomerate or coalesce in the aqueous phase and sink to the bottom of the tank, forming a liquid phosphorus phase.
- This phosphorus phase can be easily separated from the aqueous phase by gravity draining, pumping it out, decantation of the water, or other techniques. The process can be run continuously or in batches.
Landscapes
- Chemical & Material Sciences (AREA)
- Organic Chemistry (AREA)
- Life Sciences & Earth Sciences (AREA)
- Hydrology & Water Resources (AREA)
- Engineering & Computer Science (AREA)
- Environmental & Geological Engineering (AREA)
- Water Supply & Treatment (AREA)
- Inorganic Chemistry (AREA)
- Treatment Of Sludge (AREA)
- Removal Of Specific Substances (AREA)
Abstract
Description
| Sludge | Additive | Stirring | Phosphorus | Filter Cake | ||
| % | % | Weight | Rate | Time | Weight | % | Weight | % | % | ||
| Example | P | Dirt | Name | (g) | (rpm) | (min) | (g) | Rec. | (g) | P | Dirt |
| 1 | 9.7 | 26.6 | None | 0 | 0 | 60 | 3.5 | 36 | 53.7 | 10.3 | 46.6 |
| 2 | 9.6 | 25.9 | None | 0 | 200 | 60 | 2.6 | 27 | 51.7 | 9.6 | 43.8 |
| 3a | 9.5 | 26.1 | SHMP | 0.2 | 100 | 5 | 4.8 | 51 | 51.6 | 8.7 | 50.5 |
| 4b | 10.6 | 30.4 | SHMP | 0.5 | 56 | 60 | 5.6 | 53 | 60.8 | 7.7 | 48.6 |
| 5a | 9.7 | 26.2 | SHMP | 0.5 | 100 | 5 | 5.5 | 57 | 51.9 | 6.9 | 49.9 |
| 6c | 9.6 | 25.8 | SHMP | 0.5 | 200 | 60 | 4.6 | 48 | 52.8 | 8.8 | 48.6 |
| 7 | 9.8 | 26.8 | SHMP | 1.0 | 0 | 0 | 5.6 | 57 | 50.9 | 6.4 | 52.1 |
| 8d | 9.9 | 29.1 | SHMP | 1.0 | 56 | 60 | 6.5 | 66 | 56.5 | 4.7 | 49.7 |
| 9 | 10.2 | 27.0 | SHMP | 1.0 | 100 | 5 | 5.9 | 58 | 51.3 | 7.0 | 52.1 |
| 10 | 9.7 | 27.1 | SHMP | 1.0 | 100 | 15 | 5.6 | 58 | 53.9 | 6.3 | 50.0 |
| 11 | 9.6 | 26.7 | SHMP | 1.0 | 100 | 30 | 5.6 | 58 | 52.6 | 6.6 | 50.6 |
| 12 | 9.7 | 27.0 | SHMP | 1.0 | 100 | 60 | 6.3 | 65 | 49.7 | 5.3 | 52.2 |
| 13 | 8.9 | 24.8 | SHMP | 1.0 | 200 | 60 | 5.2 | 58 | 48.5 | 7.5 | 48.5 |
| 14 | 9.9 | 28.9 | SHMP | 1.5 | 56 | 60 | 6.5 | 66 | 56.0 | 5.7 | 51.2 |
| 15 | 15.2 | 31.1 | SHMP | 1.0 | 56 | 60 | 11.7 | 84 | 56.3 | 6.2 | 47.8 |
| 16 | 15.2 | 31.1 | SHMP | 1.5 | 56 | 60 | 10.8 | 71 | 48.8 | 6.3 | 61.7 |
| 17e | 10.8 | 27.0 | STPP | 1.0 | 100 | 30 | 5.9 | 55 | 50.7 | 7.9 | 53.1 |
| 18e | 10.2 | 26.7 | TSPP | 1.0 | 100 | 30 | 6.1 | 60 | 53.7 | 5.9 | 46.1 |
| 19 | 9.7 | 26.4 | TSPP/ | 0.5/ | 100 | 5 | 5.6 | 58 | 52.7 | 7.8 | 54.0 |
| SHMP | 0.5 | ||||||||||
| 20 | 10.4 | 26.6 | STPP/ | 0.5/ | 100 | 5 | 5.2 | 50 | 53.1 | 7.1 | 49.9 |
| SHMP | 0.5 | ||||||||||
| 21 | 15.2 | 31.1 | CrO3 | 1.0 | 56 | 60 | 5.1 | 34 | 62.4 | 11.2 | 48.9 |
| 22 | 15.2 | 31.1 | H2O2 | 3.4 | 56 | 60 | 4.1 | 27 | 56.5 | 15.1 | 47.1 |
| 30% | |||||||||||
| aaverage of 3 runs | |||||||||||
| baverage of 5 runs | |||||||||||
| caverage of 2 runs | |||||||||||
| daverage of 4 runs | |||||||||||
| eless coalescence; about half of the filtered phosphorus consisted of separate beads | |||||||||||
| These examples show that only about 30 wt % of the phosphorus was recovered when the sludge was filtered without the use of an additive, or when hydrogen peroxide or chromic acid were used as additives. It was possible to recover about 60 wt % phosphorus, however, when the phosphate salts of this invention were used. Greater coalescence of the phosphorus was observed when SHMP was used as the additive. | |||||||||||
Claims (20)
Priority Applications (6)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| US09/859,254 US6620396B2 (en) | 2001-05-17 | 2001-05-17 | Method of removing phosphorus from sludge |
| PCT/GB2002/001348 WO2002092517A1 (en) | 2001-05-17 | 2002-03-21 | Method of removing phosphorus from sludge |
| DE10296799T DE10296799T5 (en) | 2001-05-17 | 2002-03-21 | Process for removing phosphorus from sludge |
| CNB028101138A CN1253378C (en) | 2001-05-17 | 2002-03-21 | Method for removing phosphorus from sludge |
| CA2447123A CA2447123C (en) | 2001-05-17 | 2002-03-21 | Method of removing phosphorus from sludge |
| RU2003133286/15A RU2281911C2 (en) | 2001-05-17 | 2002-03-21 | Method of removing phosphorus from slime |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| US09/859,254 US6620396B2 (en) | 2001-05-17 | 2001-05-17 | Method of removing phosphorus from sludge |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| US20020187095A1 US20020187095A1 (en) | 2002-12-12 |
| US6620396B2 true US6620396B2 (en) | 2003-09-16 |
Family
ID=25330437
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| US09/859,254 Expired - Fee Related US6620396B2 (en) | 2001-05-17 | 2001-05-17 | Method of removing phosphorus from sludge |
Country Status (6)
| Country | Link |
|---|---|
| US (1) | US6620396B2 (en) |
| CN (1) | CN1253378C (en) |
| CA (1) | CA2447123C (en) |
| DE (1) | DE10296799T5 (en) |
| RU (1) | RU2281911C2 (en) |
| WO (1) | WO2002092517A1 (en) |
Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| US20040241073A1 (en) * | 2003-05-27 | 2004-12-02 | Glenn Springs Holdings, Inc. | A process for total environmental remediation of a phosphorus contaminated site |
Families Citing this family (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN112979109A (en) * | 2021-01-28 | 2021-06-18 | 海宁一泓环境科技有限公司 | Method for in-situ treatment of river sediment phosphorus |
Citations (9)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| US3442621A (en) | 1965-10-07 | 1969-05-06 | Monsanto Co | Phosphorus production |
| US3615218A (en) * | 1968-08-05 | 1971-10-26 | Stauffer Chemical Co | Recovery of phosphorus value from phosphorus sludge |
| US4481176A (en) * | 1983-10-03 | 1984-11-06 | Stauffer Chemical Company | Treatment for phosphorus-containing waste material |
| US4686094A (en) * | 1986-08-08 | 1987-08-11 | Stauffer Chemical Company | Treatment of pyrophoric elemental phosphorus-containing material |
| US4717558A (en) | 1986-10-29 | 1988-01-05 | Occidental Chemical Corporation | Phosphorus recovery from phosphorus-containing pond sludge |
| US5002745A (en) | 1990-05-07 | 1991-03-26 | Fmc Corporation | Method of separating and recovering phosphorus from phosphorus sludge |
| US5089142A (en) | 1990-10-30 | 1992-02-18 | Betz Laboratories, Inc. | Methods for dewatering coal and mineral concentrates |
| US5514352A (en) * | 1993-10-05 | 1996-05-07 | Hanna; John | Apparatus for high speed air oxidation of elemental phosphorous wastes in aqueous medium |
| US6451276B1 (en) * | 1999-08-10 | 2002-09-17 | Glenn Springs Holdings, Inc. | Recovery of elemental phosphorus from phosphorus sludge |
Family Cites Families (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| SU1604734A1 (en) * | 1984-12-18 | 1990-11-07 | Казахский Химико-Технологический Институт | Method of extracting phosphorus from slurry |
| RU2060932C1 (en) * | 1993-08-12 | 1996-05-27 | Акционерное общество открытого типа "Невинномысский Азот" | Method for removing phosphorous of slimes |
-
2001
- 2001-05-17 US US09/859,254 patent/US6620396B2/en not_active Expired - Fee Related
-
2002
- 2002-03-21 CA CA2447123A patent/CA2447123C/en not_active Expired - Fee Related
- 2002-03-21 WO PCT/GB2002/001348 patent/WO2002092517A1/en not_active Ceased
- 2002-03-21 CN CNB028101138A patent/CN1253378C/en not_active Expired - Fee Related
- 2002-03-21 DE DE10296799T patent/DE10296799T5/en not_active Ceased
- 2002-03-21 RU RU2003133286/15A patent/RU2281911C2/en not_active IP Right Cessation
Patent Citations (9)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| US3442621A (en) | 1965-10-07 | 1969-05-06 | Monsanto Co | Phosphorus production |
| US3615218A (en) * | 1968-08-05 | 1971-10-26 | Stauffer Chemical Co | Recovery of phosphorus value from phosphorus sludge |
| US4481176A (en) * | 1983-10-03 | 1984-11-06 | Stauffer Chemical Company | Treatment for phosphorus-containing waste material |
| US4686094A (en) * | 1986-08-08 | 1987-08-11 | Stauffer Chemical Company | Treatment of pyrophoric elemental phosphorus-containing material |
| US4717558A (en) | 1986-10-29 | 1988-01-05 | Occidental Chemical Corporation | Phosphorus recovery from phosphorus-containing pond sludge |
| US5002745A (en) | 1990-05-07 | 1991-03-26 | Fmc Corporation | Method of separating and recovering phosphorus from phosphorus sludge |
| US5089142A (en) | 1990-10-30 | 1992-02-18 | Betz Laboratories, Inc. | Methods for dewatering coal and mineral concentrates |
| US5514352A (en) * | 1993-10-05 | 1996-05-07 | Hanna; John | Apparatus for high speed air oxidation of elemental phosphorous wastes in aqueous medium |
| US6451276B1 (en) * | 1999-08-10 | 2002-09-17 | Glenn Springs Holdings, Inc. | Recovery of elemental phosphorus from phosphorus sludge |
Cited By (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| US20040241073A1 (en) * | 2003-05-27 | 2004-12-02 | Glenn Springs Holdings, Inc. | A process for total environmental remediation of a phosphorus contaminated site |
| US6955796B2 (en) * | 2003-05-27 | 2005-10-18 | Glenn Springs Holdings Company | Process for total environmental remediation of a phosphorus contaminated site |
Also Published As
| Publication number | Publication date |
|---|---|
| CN1253378C (en) | 2006-04-26 |
| CA2447123A1 (en) | 2002-11-21 |
| US20020187095A1 (en) | 2002-12-12 |
| CN1509256A (en) | 2004-06-30 |
| CA2447123C (en) | 2011-06-14 |
| WO2002092517A1 (en) | 2002-11-21 |
| DE10296799T5 (en) | 2004-10-07 |
| RU2281911C2 (en) | 2006-08-20 |
| RU2003133286A (en) | 2005-05-10 |
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Legal Events
| Date | Code | Title | Description |
|---|---|---|---|
| AS | Assignment |
Owner name: GLENN SPRINGS HOLDINGS, INC., KENTUCKY Free format text: ASSIGNMENT OF ASSIGNORS INTEREST;ASSIGNOR:SARAN, MOHAN S.;REEL/FRAME:012512/0797 Effective date: 20020116 |
|
| FPAY | Fee payment |
Year of fee payment: 4 |
|
| FPAY | Fee payment |
Year of fee payment: 8 |
|
| REMI | Maintenance fee reminder mailed | ||
| LAPS | Lapse for failure to pay maintenance fees | ||
| STCH | Information on status: patent discontinuation |
Free format text: PATENT EXPIRED DUE TO NONPAYMENT OF MAINTENANCE FEES UNDER 37 CFR 1.362 |
|
| STCH | Information on status: patent discontinuation |
Free format text: PATENT EXPIRED DUE TO NONPAYMENT OF MAINTENANCE FEES UNDER 37 CFR 1.362 |
|
| FP | Lapsed due to failure to pay maintenance fee |
Effective date: 20150916 |


